Deprecated: The each() function is deprecated. This message will be suppressed on further calls in /home/zhenxiangba/zhenxiangba.com/public_html/phproxy-improved-master/index.php on line 456
JPH0432692B2 - - Google Patents
[go: Go Back, main page]

JPH0432692B2 - - Google Patents

Info

Publication number
JPH0432692B2
JPH0432692B2 JP59046994A JP4699484A JPH0432692B2 JP H0432692 B2 JPH0432692 B2 JP H0432692B2 JP 59046994 A JP59046994 A JP 59046994A JP 4699484 A JP4699484 A JP 4699484A JP H0432692 B2 JPH0432692 B2 JP H0432692B2
Authority
JP
Japan
Prior art keywords
dialysis
dialysate
diffusion
ion exchange
exchange membrane
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Lifetime
Application number
JP59046994A
Other languages
Japanese (ja)
Other versions
JPS60193506A (en
Inventor
Hiroyuki Mishima
Koichi Toi
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Tokuyama Corp
Original Assignee
Tokuyama Corp
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Tokuyama Corp filed Critical Tokuyama Corp
Priority to JP4699484A priority Critical patent/JPS60193506A/en
Publication of JPS60193506A publication Critical patent/JPS60193506A/en
Publication of JPH0432692B2 publication Critical patent/JPH0432692B2/ja
Granted legal-status Critical Current

Links

Landscapes

  • Separation Using Semi-Permeable Membranes (AREA)

Description

【発明の詳細な説明】[Detailed description of the invention]

本発明は管状イオン交換膜を用いた拡散透析方
法に関し、特に多量の懸濁物質を含む溶液、ある
いは透析処理中に難溶性の物質を析出するような
溶液を効率よく拡散透析するに好適な拡散透析方
法を提供する。 従来、酸またはアルカリを含有する溶液から酸
またはアルカリを選択的に分離するための方法と
して、陰イオン交換膜または陽イオン交換膜を用
いた拡散透析法が知られている。特に陰イオン交
換膜を用いた酸の回収プロセスは、酸の回収率が
高いこと、工程が単純に出来ること、或いは運転
管理が容易である等、多くの利点を有するのみで
なく経済的にも優れているため、例えば鉄鋼の酸
洗液、ピツクリング廃液、電池廃酸等の処理な
ど、工業的に広く実施されている。 上記の如き処理溶液中には、浮遊した懸濁物質
(以下、SS分と略記する)を多量に含む場合が多
く、例えば鉄鋼の酸洗液中には通常数百ppm乃至
数千ppm程度のSS分を含有している。そのため、
沈降分離、凝集沈殿、あるいは過等の前処理を
行ないSS分を除去した後透析装置に供給し、酸
の回収が行なわれるが、これらの処理を行なつて
もなお充分に清澄な溶液を経済的かつ効率的に得
ることが出来ず、一部のSS分は透析装置へ供給
される。このようなSS分を含む溶液を従来用い
られている平面状のイオン交換膜を多数重ねた所
謂フイルタープレス型拡散透析装置やイオン交換
性中空繊維を束ねて用いたホローフアイバー型拡
散透析装置により拡散透析処理する場合、種々の
問題が生じる。例えば、フイルタープレス型拡散
透析装置を用いた場合、該装置内の流路、スペー
サー、配流板、イオン交換膜の表面などにSS分
が付着することが避けられず、しかも一度付着し
たSS分はほとんど離れない。また、イオン交換
性中空繊維を束ねて用いたホローフアイバー型透
析装置においても、該装置内の流路、叉は繊維表
面におけるSS分の付着による目詰りは避けられ
なかつた。このように、フイルタープレス型拡散
透析装置の流路、スペーサー、配流板、或いはイ
オン交換膜表面、或いはホローフアイバー型透析
装置の流路、中空繊維表面に溶液中のSS分が
徐々に付着・堆積すると、透析圧損の増大をきた
し、液の均一な流れを阻害するばかりでなく、酸
叉はアルカリの回収率の低下をきたし、ついには
濃度分極によるスケールトラブルなど種々の弊害
を生じ、長期にわたつての安定運転が出来なくな
る。特に、フイルタープレス型透析装置では、ス
ペーサー、配流板叉はイオン交換膜表面にSS分
が付着すると、たとえそれがわずかな量であつて
も流動抵抗が著しく増大したり、酸あるいはアル
カリの回収率が急激に低下するため、上述した問
題が顕著に現われる。この様な状態になると、透
析作業をー旦中断し、目詰りした透析装置を分
解、洗浄、再組立によつて性能蘇生を図るが、フ
イルタープレス型装置は、組立て、分解が極めて
不便であるため、多大の労力と時間を必要とする
ばかりでなく、解体作業中に取扱いを誤まると、
高価なイオン交換膜が亀裂、ピンホール等の物理
的劣化を受ける。また、解体、洗浄を頻繁に行な
うと、装置の稼動率が低下し非常に大きな損失と
なる。一方、ホローフアイバー型透析装置では、
フイルタープレス型透析装置以上にSS分に対し
て性能が劣化し易く、しかも、繊維束であるた
め、分解、洗浄による性能回復は非常に困難で、
一度SS分によつて目詰りしたら、モジユール内
の高価な中空繊維束をそつくり新品に変更しなけ
ればならず、安定運転できないばかりでなく経済
的にも大きな損失である。 また、懸濁物質を含まない溶液であつても、透
析処理を行なうと透析条件の変化によつて難溶性
の物質を析出するような溶液の場合には、透析装
置内に上記のSS分の付着による種々の弊害はさ
けられず透析処理自体を行なうことができない場
合もある。 本発明者らは、上記問題に鑑み、上記の如き溶
液を透析処理するに際し、透析処理に先だち溶液
の過、凝集沈殿、等の高度且つ複雑な前処理を
実施する必要がなく、また透析処理中に難溶性物
質を折出するような溶液であつても効率的にかつ
長期間安定して連続運転することが可能な拡散透
析方法を提供するものである。 即ち、本発明は直立した管状イオン交換膜の内
部に拡散液又は透析液を、該管状イオン交換膜の
外部に透析液又は拡散液をそれぞれ存在させて、
拡散液と透析液とを向流に流し、且つ、透析液中
に気泡を存在させることを特徴とする拡散透析方
法である。特に、直立した管状イオン交換膜で分
離された拡散室及び透析室を有する拡散透析装置
において、前記拡散室に供給する液の流れを下降
流にし、透析室に供給する液の流れを上昇流と
し、且つ透析液中に気泡を存在させる方法は、本
発明の効果が顕著であるため特に好ましい。 本発明によれば、管状イオン交換膜の管径は使
用する透析液(原液)に含有するSS分や性状に
応じて選定出来、しかもフイルタープレス型で用
いられるスペーサ、配流板等も構造上まつたく不
要であるため、目詰りが少なくしかも膜表面に
SS分が付着しにくい。また、ホローフアイバー
型よりも管径と膜間のピツチが大きく、SS分に
よる目詰りが少なく、濃度分極による性能劣化は
小さくなる。更に膜表面に付着したSS分は、透
析液中に気泡を存在させることによる液の撹乱効
果により効率的に除去される。従つて、長期に亘
つて安定的に高い透析性能を維持する事が可能と
なる。 本発明の効果は、管状イオン交換膜の形状、配
列、透析液中の気泡の形状、量などの関係等につ
いて詳しく検討した結果、初めて得られたもので
あり、単に管状イオン交換膜を用いたり、あるい
は従来のフイルタープレス型やホローフアイバー
型透析装置を用いて透析液中に気泡を存在させて
も本発明の効果は得られない。 例えば、フイルタープレス型透析装置は、スペ
ーサーや配流板を有し、且つ組立作業を容易とす
る為、該スペーサーや配流板とイオン交換膜がほ
ぼ密着した状態にあることなどから、本発明のよ
うに気泡を存在させても、該気泡が装置内、特に
スペーサーの網目内に滞留するため、本発明の効
果を発揮することは不可能である。尚、透析装置
内に気泡を存在させるという技術は、従来、フイ
ルタープレス型の電気透析装置で行なわれること
があつた。しかしながら、拡散透析における透析
液の流速は、1〜10cm/分が一般的であり、電気
透析のそれ(1〜10cm/秒)と比較して極めて遅
いこと、或いは電気透析と拡散透析では運転方法
が異なる、などのことより、単に気泡を存在させ
るだけで同じ効果を得ることは出来ない。 また、ホローフアイバー型透析装置において、
本発明の様に気泡を存在させても単位容積当りの
膜面積を大とする為即ち、繊維の単糸太さが本発
明より細くかつ高密度に充填されている為膜面に
付着したSS分の除去はほとんど不可能である。 一方、透析液中に気泡を存在させない場合に
は、いずれの型の透析装置であつても気泡による
洗浄効果が得られない為長期間の安定運転はまつ
たく不可能である。 本発明を実施する場合、透析液と拡散液は、濃
度勾配による透析効率を高めるため透析液を上昇
流にし拡散液を下降流とする向流接触が好まし
い。また、酸回収を目的とする透析処理の場合、
透析液の流量は、単位膜面積当り0.5〜3/Hr
の範囲内が好ましく透析液と拡散液の流量比は
0.5〜2.0の範囲内が好ましい。本発明によれば、
膜性能が同じであれば、膜形状によらず同一膜面
積、同一透析条件で透析液の処理が可能である。
この事は、例えば、フイルタープレス型透析装置
を本発明の透析装置に変更する場合、フイルター
プレス型透析装置に付帯するポンプやタンク等の
仕様をまつたく変更する事なく単に透析装置のみ
を本発明のものに交換する事によつて目的が達成
できる事を意味し工業上極めて意義がある。 以下、本発明の拡散透析方法について図面をも
つて詳細に説明する。 本発明に用いられる拡散透析装置は、熱交換器
等に用いられるシエル・アンド・チユーブ型と類
似のものである。即ち、直立した管状イオン交換
膜を介して拡散室と透析室が分離形成されるもの
である。代表的態様として、例えば、第1図及び
第2図に示すような金属、合成樹脂よりなる縦型
筒状容器1で、内部が2枚の管板2及び2′によ
り3つの仕切室3,3′、及び3″に区画され、管
状イオン交換膜4を介して両端の仕切室3と3゜
とが連通するように構成されるものがある。即
ち、第1図の場合斜線分が拡散室で他の部分が透
析室を示す。この際、管状イオン交換膜4は管板
2及び2′の孔に接合されるが、該接合部6は管
状イオン交換膜4の外部を流れる液と内部を流れ
る液とが漏洩による混合を生じないように接合す
ることが必要である。更に、上記装置では、中央
仕切室3′及び両端の仕切室3及び3″に液の供
給、排出を行うための供給口8,9及び排出口
7,10が付設される。上記装置により、拡散液
(一般には水又は酸、アルカリの希薄溶液)と透
析液(原液)とを向流に流し、直立したイオン交
換膜4を介して接触させるが、本発明では、透析
液を上昇流とし、拡散液を下降流として向流接触
させることが好ましく、透析液を下降流とし拡散
液を上昇流とした場合酸あるいはアルカリの回収
率を高め、効率的な分離を行なうための装置や操
作やが煩雑であるため実際的でない。また第1図
では斜線部が拡散室である態様を示したが、管状
イオン交換膜内、外のどちらを透析室にしてもよ
い。例えば、第1図とは反対に管外に透析液を流
す場合には供給口7より透析液を、一方供給口1
0より拡散液を供給し、イオン交換膜4を介して
向流接触させた後、透析液を排出口8より、ま
た、拡散液を排出口9より排出する。 本発明では、イオン交換膜を用いることが必要
である。イオン交換膜は、酸またはアルカリを選
択的にしかも高められた速度で分離する事が可能
である為、拡散透析を行なう場合には不可欠であ
る。 また使用するイオン交換膜の種類は酸と塩の分
離にあつては陰イオン交換膜を、塩基と塩の分離
にあつては陽イオン交換膜を夫々目的に応じて用
いる。これらの陽又は陰イオン交換膜は、特に限
定されず、市販のものが一般に使用し得る。即ち
陰イオン交換膜にあつては、ビニルピリジンとジ
ビニルベンゼンの共重合体或いはスチレンとジビ
ニルベンゼンの共重合体のクロルアルキル化、ア
ミノ化及び四級化などによるものがある。また陽
イオン交換膜についてはスチレンとジビニルベン
ゼンの共重合体のスルホン化等によつて得られ
る。勿論これらのイオン交換膜は適当な繊維によ
るバツキングが用いられて所謂腰の強い膜が好ま
しい。またイオン交換容量は通常0.1〜10ミリ当
量/乾燥樹脂程度の通常透析に使用される範囲の
ものが使用される。 本発明において管状イオン交換膜を用いること
は、SS分の付着を防止し、後述する気泡による
安定的な透析性能の維持を図るうえで重要であ
る。該管状イオン交換膜の寸法は、透析液の種類
や処理能力等により適宜選定されるが、一般には
内径が0.2〜10cm、長さ5〜300cmであり、特に内
径0.5〜4cm、長さ10〜200cmのものが好ましく用
いられる。管状イオン交換膜の内径が余りに小さ
いと、膜内を流れる溶液の圧力損失が大きくなる
と共に、透析液を通水した場合、SS分が目詰り
し易く、また、後述する気泡による効果がなくな
る。一方、内径が大きすぎると、単位容積当りの
膜面積が減少するため、装置を大型化する必要が
生じ、設備費及び運転費の増大を招く。また、管
状イオン交換膜の長さが短かすぎると、ワンパス
当りの酸の回収率が少なくなるため、膜の数を増
すと共に多段に接続しなければならなく、プロセ
ス設計上の不都合を生じる。一方、長すぎると、
管径を小さくした場合と同様な悪影響が生じるた
め好ましくない。 管状イオン交換膜の横断面の形状は、円又は三
角、四角、多角形等のいずれでもよいが就中、円
形のものが製膜の容易性、膜の取扱い易さ、装置
製作上より好ましい。管状イオン交換膜を製造す
る方法も制限されない。例えば、平面状イオン交
換膜を丸めて管状にし、重なり合う面を熱融着す
る方法、接着剤、シーリング剤、両面接着剤等で
接着する方法等により接合した態様;また、合成
樹脂、金属、セラミツク等からなる編組み管や多
孔性管をイオン交換膜の支持体とし、これにモノ
マーを塗布(含浸)、重合、イオン交換基導入な
どの手順を経て管状膜とした態様;あるいは、多
孔性管の細孔内にイオン交換樹脂を充填した態様
等が挙げられる。該管状イオン交換膜の数及び管
板に対する配置は、溶液の種類、処理量、酸の回
収率等より適宜選定されるが、管状膜同士がお互
いに接触しない様に配置する。例えば、管状イオ
ン交換膜群の配置は、管板に対して正方形、ある
いは正三角形に、又、管状イオン交換膜の数は、
プロセス設計、製作、メンテナンス等の面より筒
状容器全断面積の5〜70%が好ましい。また、管
状イオン交換膜を管板の孔に接合する方法も例え
ば、管状イオン交換膜を直接管板の孔の外部に接
着剤、シーリング剤等で接合する方法や管板の孔
にネジを切り、管板の孔内に入れたパツキングを
介してナツトで締める方法等があるが、特に拡散
透析では、単位膜面積当りの供給量が一般に、
0.5〜3/Hm2と少なくしかも配流板やスペー
サーがない為透析液と拡散液との2液間の圧力差
が非常に小さく管状イオン交換膜による接合は極
めて簡単となる。 本発明において最も大きな特徴は、透析液中に
気泡を存在させつつ拡散透析することである。 本発明によれば、上昇する透析液中に気泡を存
在させることにより、該気泡を含む透析液(気泡
群)が蛇行しながら上昇するため、その撹拌効果
により、膜表面に付着したSS分を効率的に除去
することができる。従つて、本発明における気泡
の存在とは、単に拡散透析することに伴う気体で
なく、外部から強制的に吹き込んだ気泡の存在を
意味する。 透析液中に気泡を存在させる方法は特に制限さ
れない。例えば、第1図及び第2図に示す如く、
透析装置内の下端仕切室3内に散気管11等を設
け、該散気管により透析液中に気体を吹き込む方
法、或いは外部のタンク内等で高せん断力を作用
させつつ撹拌する方法や液中に高速で気体を送入
する方法等により、予め気泡を存在させた透析液
を拡散透析装置へ供給する方法等がある。いずれ
の方法においても、本発明の効果を発揮させるた
めには、気泡の供給量は重要で、一般に気体の存
在液に対する線速度は0.1〜10m/分で適宜選定
することが好ましい。上記線速度が小さすぎる
と、気泡による洗浄効果が十分でなく、又、大き
すぎると運転効率が低下するばかりでなく十分な
洗浄効果が得られない。 上記した気体の吹込みに用いられる散気管11
には、気体を液中に吹込むための散気孔12が設
けられており、該散気管により吹き込まれた気体
は、上端仕切室3″において気液分離され、ガス
抜口13より装置外へ排気される。散気管11
は、合成樹脂、金属、セラミツク等からなる多孔
性あるいはメツシユ状のものや、パイプの側面に
多数孔をあけたもの等が用いられるが、いずれの
場合も、その全長に亘つて均一に気体を噴出し、
管状イオン交換膜群に均等に気体を供給できるも
のが好ましい。 散気管よりの気体の吹き込みは、連続的又は間
けつ的に行ない、後者にあつては定期的あるいは
不定期的に行なうことが出来る。いずれの場合
も、透析液中のSS分の性状、量、あるいは透析
装置の構造、透析条件及び膜面へのSS分の付着
量等により適宜決定される。通常、1〜100時間
に1回の割合で1〜30分吹き込めばよい。 本発明においては、管状イオン交換膜内(チユ
ーブ側)に透析液を供給する態様、逆に管状イオ
ン交換膜外(シエル側)に透析液を供給する態様
のいずれの態様も採用でき、いずれの方法を採用
するかは、透析液の性状や透析装置の構造等によ
り適宜選定される。いずれの場合でも、透析液中
に気泡を存在させることが大切で、拡散液中に気
泡を存在させた場合には気泡を存在させない場合
に較べて、若干の効果は期待できるが、本発明と
同等の効果を発揮させることは困難である。 その他、本発明に用いる装置の各部の材質、形
状及び構成方法等については、上記要件を満足す
る範囲内で適宜選定すればよい。又、気体も、空
気、窒素等、不活性ガスが一般に用いられ、就中
空気が最も好適に用いられる。 以上の説明により理解される如く、本発明によ
れば従来のフイルタープレス型やホローフアイバ
ー型で行なわれている高度な前処理をまつたく必
要とせずまた透析処理中の反応によつて透析液中
に難溶性の沈殿や結晶を生じる場合であつても、
長期に亘つて安定した状態で連続運転が出来る。
そのため、透析装置の停止及び解体、洗浄等に費
やす費用も少なくてすみ有利な透析方法である。
更に、透析装置の運転操作や管理を極めて容易に
する等、計り知れない効果をもたらすものであ
る。 以下、本発明の実施例を示す。 実施例 1 硫酸を含む鉄鋼廃酸は、鋼材表面のスケール分
としてシリカ、カーボン等のSS分を500〜
2000ppmと非常に多く含む。上記廃酸を拡散透析
するに際し、フイルタープレス型透析装置及び、
ホローフアイバー型透析装置による透析方法と本
発明の透析方法とを比較する実施を行なつた。使
用した三種類の透析装置の仕様を以下に示すが、
いずれも同一膜面積を有する。 フイルタープレス型透析装置 陰イオン交換膜がガスケツトとスペーサーを
介して交互に62対積層してスタツクを構成しそ
の両端に給液枠兼締付枠をおき締付ボルトで締
付けて拡散透析装置を構成した。 有効膜面積 幅20cm×長さ50cm 透析室数 透析室 63室 拡散室62室 全有効膜面積 6.2m2 ガスケツト厚み、材質 透析室 2ミリ(ネ
オプレン等) 拡散室 1ミリ(ネオプレン等) イオン交換膜 徳山曹達(株)製 ネオプセタ AFN(商品名) スペーサー ポリエチレン製斜交網 ホローフアイバー型透析装置 陰イオン交換性中空繊維をその両端開口部を
揃えて束ね、接着剤を用いて両端の開口部で各
繊維中空部を残して接着した中空繊維群を筒状
容器内に収容しホローフアイバー型拡散透析装
置を構成した。 中空繊維寸法 外径 0.5mm×内径0.3mm 有効膜面積 6.2m2 筒状容器の寸法 外径200mm×長さ450mm 本発明の管型透析装置 上記したホローフアイバー型透析装置と同じ
構造を有するが、用いる管状膜の寸法は内径10
ミリ、膜間のピツチは15ミリで正方形配列で配
置した。 管状イオン交換膜の形状、寸法 断面;円形 寸法;内径10ミリ×長さ1000ミリ×厚み0.15ミ
リ 本数;196本 管状膜の配列 配列;正方形 ピツチ;15ミリ 透析装置本体の寸 寸法;幅230ミリ×奥行230
ミリ×高さ1300ミリ 有効膜面積 6.2m2 上記の透析装置の運転方法、透析条件は次の通
りである。
The present invention relates to a diffusion dialysis method using a tubular ion exchange membrane, and is particularly suitable for efficient diffusion dialysis of solutions containing a large amount of suspended solids or solutions that precipitate poorly soluble substances during dialysis treatment. Provides a dialysis method. Conventionally, a diffusion dialysis method using an anion exchange membrane or a cation exchange membrane is known as a method for selectively separating acids or alkalis from solutions containing acids or alkalis. In particular, acid recovery processes using anion exchange membranes not only have many advantages, such as high acid recovery rates, simple processes, and easy operation management, but are also economically viable. Because of its excellent properties, it is widely used industrially, for example, in the treatment of steel pickling liquid, pickling waste liquid, battery waste acid, etc. The above-mentioned processing solution often contains a large amount of suspended solids (hereinafter abbreviated as SS). For example, a steel pickling solution usually contains several hundred ppm to several thousand ppm. Contains SS. Therefore,
After pretreatment such as sedimentation separation, coagulation sedimentation, or filtration is performed to remove the SS content, it is supplied to a dialysis machine and the acid is recovered, but even after these treatments, a sufficiently clear solution cannot be economically produced. Therefore, some SS is supplied to the dialysis machine. A solution containing such an SS component is diffused using a conventionally used so-called filter press type diffusion dialysis device in which many planar ion exchange membranes are stacked or a hollow fiber type diffusion dialysis device in which ion exchange hollow fibers are bundled. Various problems arise when performing dialysis treatment. For example, when a filter press type diffusion dialysis device is used, it is inevitable that SS components will adhere to the channels, spacers, flow plates, ion exchange membrane surfaces, etc. inside the device, and once the SS components have adhered, I almost never leave. Furthermore, even in a hollow fiber type dialysis device using a bundle of ion-exchangeable hollow fibers, clogging due to adhesion of SS components in the channel within the device or on the surface of the fibers was unavoidable. In this way, the SS content in the solution gradually adheres and accumulates on the flow path, spacer, flow plate, or ion exchange membrane surface of a filter press type diffusion dialysis device, or on the flow path and hollow fiber surface of a hollow fiber type dialysis device. This not only increases the dialysis pressure drop and impedes the uniform flow of the solution, but also reduces the recovery rate of acid or alkali, and eventually causes various problems such as scale troubles due to concentration polarization, which can lead to long-term problems. Stable operation becomes impossible. In particular, in filter press type dialysis equipment, if SS content adheres to the spacer, flow plate, or ion exchange membrane surface, even if it is only a small amount, the flow resistance will increase significantly, and the recovery rate of acid or alkali will increase. The above-mentioned problem becomes conspicuous because of the sudden decrease in When this happens, dialysis work is temporarily interrupted and the clogged dialysis machine is disassembled, cleaned, and reassembled to restore its performance, but filter press machines are extremely inconvenient to assemble and disassemble. Therefore, not only does it require a great deal of labor and time, but if handled incorrectly during demolition work,
Expensive ion exchange membranes are subject to physical deterioration such as cracks and pinholes. Furthermore, frequent disassembly and cleaning will reduce the operating rate of the equipment, resulting in a very large loss. On the other hand, in the hollow-eye dialysis machine,
Performance deteriorates more easily than filter press type dialysis equipment due to SS content, and since it is a fiber bundle, it is extremely difficult to restore performance by disassembling and cleaning.
Once clogged with SS, the expensive hollow fiber bundles in the module must be warped and replaced with new ones, which not only prevents stable operation but also causes a huge economic loss. In addition, even if the solution does not contain suspended solids, if the solution is one in which poorly soluble substances are precipitated due to changes in dialysis conditions during dialysis treatment, the above SS content may be added to the dialysis machine. Various adverse effects due to adhesion cannot be avoided, and dialysis treatment itself may not be possible in some cases. In view of the above problems, the present inventors have discovered that when performing dialysis treatment on a solution such as that described above, there is no need to perform sophisticated and complicated pretreatments such as filtration of the solution, coagulation and precipitation prior to dialysis treatment, and The purpose of the present invention is to provide a diffusion dialysis method that can be operated efficiently and stably continuously for a long period of time even when using a solution in which poorly soluble substances are precipitated. That is, in the present invention, a diffusion liquid or a dialysing liquid is present inside an upright tubular ion exchange membrane, and a dialysing liquid or a diffusion liquid is present outside the tubular ion exchange membrane,
This is a diffusion dialysis method characterized by flowing a diffusion liquid and a dialysate in countercurrent flow, and by allowing air bubbles to exist in the dialysate. In particular, in a diffusion dialysis apparatus having a diffusion chamber and a dialysis chamber separated by an upright tubular ion exchange membrane, the flow of the liquid supplied to the diffusion chamber is made into a downward flow, and the flow of the liquid supplied to the dialysis chamber is made into an upward flow. , and a method in which air bubbles are present in the dialysate is particularly preferred because the effects of the present invention are significant. According to the present invention, the diameter of the tubular ion exchange membrane can be selected depending on the SS content and properties of the dialysate (undiluted solution) used, and the spacers, flow plates, etc. used in the filter press type can also be selected depending on the structure. Since there is no need for a lot of water, there is less clogging and there is no need to clean the membrane surface.
SS content is difficult to adhere to. In addition, the pipe diameter and the pitch between the membranes are larger than the hollow fiber type, so there is less clogging due to SS components, and performance deterioration due to concentration polarization is reduced. Furthermore, the SS components adhering to the membrane surface are efficiently removed by the liquid disturbance effect caused by the presence of air bubbles in the dialysate. Therefore, it is possible to stably maintain high dialysis performance over a long period of time. The effects of the present invention were obtained for the first time as a result of detailed studies on the relationship between the shape and arrangement of tubular ion exchange membranes, and the shape and amount of bubbles in dialysate. Alternatively, even if air bubbles are present in the dialysate using a conventional filter press type or hollow fiber type dialysis device, the effects of the present invention cannot be obtained. For example, a filter press type dialysis device has a spacer and a flow distribution plate, and in order to facilitate the assembly work, the spacer and flow distribution plate are in close contact with the ion exchange membrane. Even if air bubbles are present in the device, the effects of the present invention cannot be achieved because the air bubbles remain within the device, particularly within the mesh of the spacer. Note that the technique of creating air bubbles in a dialysis device has conventionally been carried out in a filter press type electrodialysis device. However, the flow rate of the dialysate in diffusion dialysis is generally 1 to 10 cm/min, which is extremely slow compared to that in electrodialysis (1 to 10 cm/sec), or the operating method is different between electrodialysis and diffusion dialysis. It is not possible to obtain the same effect simply by allowing bubbles to exist, for example, because the bubbles are different. In addition, in hollow-eye dialysis equipment,
In order to increase the membrane area per unit volume even if bubbles are present as in the present invention, in other words, the single fiber thickness is thinner and densely packed than in the present invention, so SS adhered to the membrane surface. Removal of minutes is almost impossible. On the other hand, if no air bubbles are present in the dialysate, stable operation over a long period of time is impossible for any type of dialysis apparatus because the air bubbles do not provide the cleaning effect. When carrying out the present invention, the dialysate and the diffusion liquid are preferably brought into countercurrent contact, with the dialysate flowing upward and the diffusion liquid flowing downward, in order to increase the dialysis efficiency due to the concentration gradient. In addition, in the case of dialysis treatment for the purpose of acid recovery,
The flow rate of dialysate is 0.5 to 3/Hr per unit membrane area.
The flow rate ratio of dialysate and diffusion liquid is preferably within the range of
It is preferably within the range of 0.5 to 2.0. According to the invention,
As long as the membrane performance is the same, the dialysate can be treated with the same membrane area and under the same dialysis conditions regardless of the membrane shape.
This means that, for example, when changing a filter press type dialysis device to the dialysis device of the present invention, only the dialysis device of the present invention can be changed without completely changing the specifications of the pump, tank, etc. attached to the filter press type dialysis device. It means that a goal can be achieved by exchanging it for something else, and it is of great industrial significance. Hereinafter, the diffusion dialysis method of the present invention will be explained in detail with reference to the drawings. The diffusion dialysis device used in the present invention is similar to a shell and tube type used in heat exchangers and the like. That is, the diffusion chamber and the dialysis chamber are formed separately through an upright tubular ion exchange membrane. As a typical embodiment, for example, a vertical cylindrical container 1 made of metal or synthetic resin as shown in FIGS. 1 and 2 has three partitions 3, 3', and 3'', and the partition chamber 3 at both ends communicates with 3° through the tubular ion exchange membrane 4. In other words, in the case of FIG. Another part of the chamber represents a dialysis chamber, where the tubular ion exchange membrane 4 is joined to the holes in the tube plates 2 and 2', and the joint 6 is connected to the liquid flowing outside the tubular ion exchange membrane 4. It is necessary to connect the liquid flowing inside to prevent mixing due to leakage.Furthermore, in the above device, the liquid is supplied to and discharged from the central partition 3' and the partitions 3 and 3'' at both ends. Supply ports 8, 9 and discharge ports 7, 10 are provided for this purpose. With the above device, the diffusion liquid (generally water or a dilute solution of an acid or alkali) and the dialysate (undiluted solution) are caused to flow countercurrently and brought into contact with each other through the upright ion exchange membrane 4. In the present invention, the dialysate It is preferable to make countercurrent contact with the dialysate as an upward flow and the diffusion liquid as a downward flow.If the dialysate is a downward flow and the diffusion liquid is an upward flow, the recovery rate of acid or alkali can be increased and efficient separation can be achieved. It is not practical because the equipment and operations are complicated. Although FIG. 1 shows an embodiment in which the diagonally shaded area is the diffusion chamber, either the inside or outside of the tubular ion exchange membrane may be used as the dialysis chamber. For example, if the dialysate is to flow outside the tube, contrary to FIG.
After supplying the diffusion liquid from 0 and bringing it into countercurrent contact through the ion exchange membrane 4, the dialysate is discharged from the discharge port 8, and the diffusion liquid is discharged from the discharge port 9. The present invention requires the use of an ion exchange membrane. Ion exchange membranes are essential when performing diffusion dialysis because they allow acids or alkalis to be separated selectively and at an increased rate. Regarding the type of ion exchange membrane used, an anion exchange membrane is used for separating acids and salts, and a cation exchange membrane is used for separating bases and salts, depending on the purpose. These cation or anion exchange membranes are not particularly limited, and commercially available ones can generally be used. That is, anion exchange membranes include those produced by chloroalkylation, amination, and quaternization of a copolymer of vinylpyridine and divinylbenzene or a copolymer of styrene and divinylbenzene. Further, the cation exchange membrane can be obtained by sulfonation of a copolymer of styrene and divinylbenzene. Of course, it is preferable that these ion-exchange membranes are so-called stiff membranes that are backed by suitable fibers. The ion exchange capacity used is usually 0.1 to 10 milliequivalents/dry resin, which is within the range normally used for dialysis. The use of a tubular ion exchange membrane in the present invention is important in preventing the adhesion of SS components and maintaining stable dialysis performance due to air bubbles, which will be described later. The dimensions of the tubular ion exchange membrane are appropriately selected depending on the type of dialysate, processing capacity, etc., but generally the inner diameter is 0.2 to 10 cm and the length is 5 to 300 cm, particularly the inner diameter is 0.5 to 4 cm and the length is 10 to 300 cm. A length of 200 cm is preferably used. If the inner diameter of the tubular ion exchange membrane is too small, the pressure loss of the solution flowing through the membrane will be large, and when dialysate is passed through the membrane, the SS content will easily clog, and the effect of air bubbles, which will be described later, will be lost. On the other hand, if the inner diameter is too large, the membrane area per unit volume will decrease, making it necessary to increase the size of the device, leading to increased equipment costs and operating costs. Furthermore, if the length of the tubular ion exchange membrane is too short, the acid recovery rate per pass will be low, which will require an increase in the number of membranes and the need to connect them in multiple stages, resulting in inconveniences in process design. On the other hand, if it is too long,
This is not preferable because it causes the same adverse effects as when the pipe diameter is made smaller. The cross-sectional shape of the tubular ion-exchange membrane may be circular, triangular, square, polygonal, etc., but circular is particularly preferred from the viewpoint of ease of membrane formation, ease of membrane handling, and device fabrication. The method of manufacturing the tubular ion exchange membrane is also not limited. For example, a planar ion-exchange membrane is rolled into a tubular shape, and the overlapping surfaces are bonded by heat-sealing, adhesive, sealant, double-sided adhesive, etc.; An embodiment in which a braided tube or a porous tube consisting of the Examples include an embodiment in which ion exchange resin is filled into the pores of the ion exchange resin. The number of tubular ion-exchange membranes and their arrangement with respect to the tube plate are appropriately selected depending on the type of solution, throughput, acid recovery rate, etc., but the tubular membranes are arranged so that they do not come into contact with each other. For example, the arrangement of the tubular ion exchange membranes may be square or equilateral with respect to the tube plate, and the number of tubular ion exchange membranes may be
From the viewpoint of process design, manufacturing, maintenance, etc., it is preferable that the cross-sectional area of the cylindrical container be 5 to 70%. There are also methods for joining the tubular ion-exchange membrane to the holes in the tubesheet, such as joining the tubular ion-exchange membrane directly to the outside of the holes in the tubesheet with an adhesive or sealant, or cutting screws into the holes in the tubesheet. There are methods such as tightening with nuts through packing inserted into the holes in the tube plate, but especially in diffusion dialysis, the amount supplied per unit membrane area is generally
The pressure difference between the dialysate and the diffusion liquid is very small, which is as low as 0.5 to 3/ Hm2 , and there is no flow plate or spacer, making joining using the tubular ion exchange membrane extremely simple. The most significant feature of the present invention is that diffusion dialysis is performed while bubbles are present in the dialysate. According to the present invention, by allowing air bubbles to exist in the rising dialysate, the dialysate containing the air bubbles (bubbles group) rises in a meandering manner, and its stirring effect removes the SS adhering to the membrane surface. It can be removed efficiently. Therefore, the presence of air bubbles in the present invention means the presence of air bubbles forcibly blown in from the outside, rather than simply gas accompanying diffusion dialysis. There are no particular restrictions on the method for creating air bubbles in the dialysate. For example, as shown in Figures 1 and 2,
A method in which an aeration pipe 11 or the like is provided in the lower end partition 3 of the dialysis machine, and gas is blown into the dialysate using the aeration pipe, or a method in which the dialysate is stirred while applying high shear force in an external tank, etc. There is a method of supplying a dialysate in which air bubbles are made to exist in advance to a diffusion dialysis device by, for example, introducing gas at high speed. In either method, the amount of bubbles supplied is important in order to exhibit the effects of the present invention, and it is generally preferable to appropriately select the linear velocity relative to the liquid containing gas from 0.1 to 10 m/min. If the linear velocity is too low, the cleaning effect due to bubbles will not be sufficient, and if it is too high, not only will the operating efficiency decrease, but also a sufficient cleaning effect will not be obtained. Diffuser pipe 11 used for blowing the above gas
is provided with an air diffuser hole 12 for blowing gas into the liquid, and the gas blown through the air diffuser pipe is separated into gas and liquid in the upper partition chamber 3'', and is exhausted to the outside of the apparatus through the gas vent 13. Diffusion pipe 11
Porous or mesh-like pipes made of synthetic resin, metal, ceramic, etc., or pipes with many holes drilled on the side of the pipe are used, but in either case, the gas can be uniformly distributed over the entire length of the pipe. gush,
It is preferable to use one that can evenly supply gas to the tubular ion exchange membrane group. The gas can be blown into the air diffuser continuously or intermittently, and in the case of the latter, it can be done regularly or irregularly. In either case, it is determined as appropriate based on the properties and amount of SS in the dialysate, the structure of the dialysis device, dialysis conditions, the amount of SS attached to the membrane surface, etc. Normally, it is sufficient to blow for 1 to 30 minutes once every 1 to 100 hours. In the present invention, it is possible to adopt either a mode in which the dialysate is supplied inside the tubular ion exchange membrane (tube side) or a mode in which the dialysate is supplied outside the tubular ion exchange membrane (shell side). The method to be adopted is appropriately selected depending on the properties of the dialysate, the structure of the dialysis apparatus, etc. In either case, it is important to have air bubbles present in the dialysate, and when air bubbles are present in the diffusion liquid, a slight effect can be expected compared to the case where no air bubbles are present. It is difficult to achieve the same effect. In addition, the material, shape, construction method, etc. of each part of the device used in the present invention may be appropriately selected within a range that satisfies the above requirements. As for the gas, inert gases such as air and nitrogen are generally used, and air is most preferably used. As can be understood from the above explanation, according to the present invention, there is no need for the advanced pretreatment performed in the conventional filter press type or hollow fiber type, and the dialysis fluid can be absorbed into the dialysate by the reaction during the dialysis treatment. Even if it produces poorly soluble precipitates or crystals,
Continuous operation is possible in a stable condition for a long period of time.
Therefore, it is an advantageous dialysis method that requires less expense for stopping, dismantling, and cleaning the dialysis equipment.
Furthermore, it brings about immeasurable effects, such as making the operation and management of the dialysis machine extremely easy. Examples of the present invention will be shown below. Example 1 Steel waste acid containing sulfuric acid has a SS content of silica, carbon, etc. from 500 to 500 as the scale content on the steel surface.
Contains a very large amount of 2000ppm. When carrying out diffusion dialysis of the waste acid, a filter press type dialysis device and
A comparison was made between a dialysis method using a hollow fiber type dialysis device and the dialysis method of the present invention. The specifications of the three types of dialysis machines used are shown below.
Both have the same membrane area. Filter press type dialysis device 62 pairs of anion exchange membranes are stacked alternately via gaskets and spacers to form a stack, and a liquid supply frame/tightening frame is placed at both ends of the stack and tightened with tightening bolts to form a diffusion dialysis device. did. Effective membrane area Width 20cm x length 50cm Number of dialysis rooms Dialysis rooms 63 rooms Diffusion rooms 62 rooms Total effective membrane area 6.2m 2 Gasket thickness, material Dialysis room 2mm (Neoprene, etc.) Diffusion room 1mm (Neoprene, etc.) Ion exchange membrane Manufactured by Tokuyama Soda Co., Ltd. Neopceta AFN (product name) Spacer Polyethylene diagonal mesh Hollow fiber type dialysis device Anion-exchange hollow fibers are bundled with the openings at both ends aligned, and each opening at both ends is tied together using adhesive. A group of hollow fibers that were glued together with the fiber hollow portions left open was housed in a cylindrical container to construct a hollow fiber type diffusion dialysis device. Hollow fiber dimensions: Outer diameter: 0.5 mm x inner diameter: 0.3 mm Effective membrane area: 6.2 m Dimensions of 2 cylindrical containers: Outer diameter: 200 mm x length: 450 mm The tubular dialysis device of the present invention has the same structure as the hollow fiber dialysis device described above, but The tubular membrane used has an inner diameter of 10
The membranes were arranged in a square array with a pitch of 15 mm. Shape and dimensions of tubular ion exchange membranes Cross section; Circular dimensions; Inner diameter 10 mm x Length 1000 mm x Thickness 0.15 mm Number of tubes: 196 Main tubular membrane arrangement Arrangement; Square pitch; 15 mm Dimensions of the dialysis machine body Dimensions: Width 230 mm ×Depth 230
mm x height 1300 mm Effective membrane area 6.2 m 2 The operating method and dialysis conditions of the above dialysis machine are as follows.

【表】 透析液、拡散液両液とも25℃に温度調整し、一
過処理で連続的に透析装置に供給後系外に排出し
た。 また、いずれの装置とも装置内の透析液に空気
を供給するための配管を設けた。即ち、フイル
タープレス型透析装置では、透析液を供給する給
液枠の入口部直前に空気供給配管を設けた。ホ
ローフアイバー型透析装置では、筒状容器の中央
仕切室下部外周に空気供給配管を8ケ所設けた。
本発明の管型透析装置では、下端仕切室内に設
けられた多孔板よりイオン交換膜群へ均一に分散
供給した。空気の供給量は、定期的かつ間欠的に
行ない12時間毎に5分間そして供給量は、空塔線
速度で1m/分であつた。 上記の装置、透析条件にて廃酸の回収実験を行
ない酸の回収率と透析室入口圧の経時変化を第1
表に示す。尚、酸回収率は、次の式で求めたもの
である。 回収率=拡散液中の酸濃度×拡散液の容積/透析液中
の酸濃度×透析液の容積
[Table] The temperature of both the dialysate and the diffusion liquid was adjusted to 25°C, and they were continuously supplied to the dialysis machine using a one-time process and then discharged from the system. In addition, each device was equipped with piping for supplying air to the dialysate inside the device. That is, in the filter press type dialysis apparatus, an air supply pipe is provided immediately before the inlet of the liquid supply frame that supplies the dialysate. In the hollow fiber type dialysis device, air supply pipes were provided at eight locations around the outer periphery of the lower part of the central partition of the cylindrical container.
In the tubular dialysis apparatus of the present invention, the ion exchange membranes are uniformly distributed and supplied through the perforated plate provided in the lower end partition. The air supply was periodically and intermittently for 5 minutes every 12 hours, and the supply was at a superficial linear velocity of 1 m/min. A waste acid recovery experiment was conducted using the above equipment and dialysis conditions, and the acid recovery rate and the change in dialysis chamber inlet pressure over time were first investigated.
Shown in the table. Note that the acid recovery rate was determined using the following formula. Recovery rate = acid concentration in the diffusion liquid x volume of the diffusion liquid / acid concentration in the dialysate x volume of the dialysate

【表】 *は比較例を示す。
フイルタープレス型、ホローフアイバー型
透析装置では、SS分の多い透析液をまつたく前
処理することなく透析装置に供給すると入口配流
板や中空繊維束が多量のSSにより短時間で目詰
りし、長期間の運転を行なう事ができない。そこ
で、フイルタープレス型では凝集沈殿、砂
過、10ミクロンカツトのカートリツジフイルター
からなる前処理を実施しSS分を1ppm以下まで除
濁した。ホローフアイバー型では、さらに1ミ
リクロンカツトのカートリツジフイルターを設け
4次処理を実施した。この様に処理した透析液を
用いてNo.1〜6とまつたく同一装置、同一透析条
件で酸の回収実験を行ない、酸回収率と入口圧の
経時変化を調べ第2表に示す。
[Table] * indicates a comparative example.
In filter press type and hollow fiber type dialysis machines, if dialysate with a high SS content is supplied to the dialysis machine without thorough pretreatment, the inlet distribution plate and hollow fiber bundles will be clogged with a large amount of SS in a short period of time, resulting in long-term problems. Unable to drive for a period of time. Therefore, in the filter press type, pretreatment consisting of coagulation sedimentation, sand filtration, and a 10 micron cut cartridge filter was performed to remove the SS content to 1 ppm or less. In the hollow fiber type, a 1 micron cut cartridge filter was further installed to perform the fourth treatment. Using the dialysate treated in this way, an acid recovery experiment was conducted using the same apparatus and under the same dialysis conditions as Nos. 1 to 6, and the changes in acid recovery rate and inlet pressure over time were investigated and are shown in Table 2.

【表】【table】

【表】 実施例 2 硝酸と弗酸を含むステンレスの洗浄廃酸中に
は、SS分が100〜200ppm含まれる。実験に用い
た洗浄廃酸の組成は、硝酸100g/、沸酸15
g/の混合溶液である。かかる洗浄廃酸に対し
て、実施例1とまつたく同一な透析装置、透析条
件、前処理条件にて本発明の透析方法を実施し
た。 その結果、拡散液中の酸回収率は第3表に示す
通りであつた。
[Table] Example 2 Stainless steel cleaning waste acid containing nitric acid and hydrofluoric acid contains 100 to 200 ppm of SS. The composition of the cleaning waste acid used in the experiment was 100 g of nitric acid and 15 g of boiling acid.
It is a mixed solution of g/g/. The dialysis method of the present invention was carried out on the washed waste acid using the same dialysis apparatus, dialysis conditions, and pretreatment conditions as in Example 1. As a result, the acid recovery rate in the diffusion liquid was as shown in Table 3.

【表】【table】

【表】 回収率の上段は硝酸、下段は弗酸を示す
*は比較例を示す。
[Table] The upper row of recovery rates shows nitric acid, and the lower row shows hydrofluoric acid. * indicates a comparative example.

【図面の簡単な説明】[Brief explanation of drawings]

第1図及び第2図は、本発明に用いる装置の代
表的態様を示す図である。図において、1は竪型
筒状容器、2(及び2′)は管板、3(3′及び
3″)は仕切室、4は管状イオン交換膜、5は孔、
6は接合部、7,8,9,10は供給口又は排出
口、11は散気管、12は散気孔、13はガス抜
口である。
FIGS. 1 and 2 are diagrams showing typical embodiments of the apparatus used in the present invention. In the figure, 1 is a vertical cylindrical container, 2 (and 2') is a tube plate, 3 (3' and 3'') is a partition, 4 is a tubular ion exchange membrane, 5 is a hole,
6 is a joint, 7, 8, 9, and 10 are supply ports or exhaust ports, 11 is an aeration tube, 12 is an aeration hole, and 13 is a gas outlet.

Claims (1)

【特許請求の範囲】[Claims] 1 直立した管状イオン交換膜の内部に拡散液又
は透析液を、該管状イオン交換膜の外部に透析液
又は拡散液をそれぞれ存在させて、拡散液と透析
液とを向流に流し、且つ、透析液中に気泡を存在
させることを特徴とする拡散透析方法。
1. A diffusion liquid or a dialysate is present inside an upright tubular ion exchange membrane, and a dialysate or a diffusion liquid is present outside the tubular ion exchange membrane, and the diffusion liquid and the dialysate flow countercurrently, and A diffusion dialysis method characterized by the presence of air bubbles in the dialysate.
JP4699484A 1984-03-14 1984-03-14 Diffusion dialysis method Granted JPS60193506A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP4699484A JPS60193506A (en) 1984-03-14 1984-03-14 Diffusion dialysis method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP4699484A JPS60193506A (en) 1984-03-14 1984-03-14 Diffusion dialysis method

Publications (2)

Publication Number Publication Date
JPS60193506A JPS60193506A (en) 1985-10-02
JPH0432692B2 true JPH0432692B2 (en) 1992-06-01

Family

ID=12762745

Family Applications (1)

Application Number Title Priority Date Filing Date
JP4699484A Granted JPS60193506A (en) 1984-03-14 1984-03-14 Diffusion dialysis method

Country Status (1)

Country Link
JP (1) JPS60193506A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US8925624B2 (en) 2010-04-09 2015-01-06 Denso Corporation Exhaust heat exchanger

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61167907U (en) * 1985-04-05 1986-10-18

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5950366B2 (en) * 1976-05-26 1984-12-07 株式会社日立製作所 dialysis machine

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US8925624B2 (en) 2010-04-09 2015-01-06 Denso Corporation Exhaust heat exchanger

Also Published As

Publication number Publication date
JPS60193506A (en) 1985-10-02

Similar Documents

Publication Publication Date Title
EP1527810B1 (en) A permeate collection assembly
JP4382821B2 (en) Membrane module and integrated membrane cassette
US7022231B2 (en) Apparatus incorporating potted hollow fiber membranes
US6682652B2 (en) Apparatus for withdrawing permeate using an immersed vertical skein of hollow fiber membranes
EP1598105B1 (en) Hollow fiber membrane module and module arrangement group thereof
US7537701B2 (en) Membrane filtration module with adjustable header spacing
CA1255074A (en) Method and apparatus for contacting reactants in chemical and biological reactions
US20100326897A1 (en) Membrane filtration module with adjustable header spacing
NZ228510A (en) Membrane separation system: membranes partially immersed in permeate
JPH0432692B2 (en)
EP1213048B2 (en) Method of potting fiber membranes
EP0387270B1 (en) Transfer membrane apparatus
CN113832018B (en) Ceramic polymer membrane equipment for preparing enzyme technology
CN213357186U (en) A mobile container water making equipment
WO2007043879A1 (en) Apparatus for the purification of water and a method for its use
KR101685356B1 (en) Vertical Type Hollow Fiber Membrane Module and Filtering System Using The Same
CN113522031A (en) Electrodialysis membrane stack ware
JPS61200808A (en) Apparatus for filtering solution
JPS6382B2 (en)
AU2005311248B2 (en) Filtering system for water and waste water
CN222788952U (en) Detachable large-flux flat ceramic membrane assembly based on densely placed single sheets
CN212712856U (en) High-efficiency mixed ion exchanger
CN101264423B (en) Membrane separation equipment
JPS61181503A (en) Apparatus for filtering solution
CN212334876U (en) Electrolysis-ion exchange purifies extrinsic cycle production system